298 94 307/02 Untersuchungen zum Stand der Umsetzung des ...
298 94 307/02 Untersuchungen zum Stand der Umsetzung des ... 298 94 307/02 Untersuchungen zum Stand der Umsetzung des ...
Teil 3 Seite 4-51 In the region of 30 –50% of the effluent receives anaerobic pre-treatment (down-flow cir- culation reactor, Laran system of the company Linde). Although the effluent exhibits a relatively high BSB5:N ratio at 7:1 in relation to other animal carcass disposal plant efflu- ent, as a rule, just enough organic carbon remains for de-nitrification, but can be in short supply on some occasions. At a biomass concentration of approx. 7 to 8 g/l the BSB5 sludge load is 0,05 kg/(kg×d). The internal cycle is set to 300 to 400%. The BSB5:N ratio, the BSB5 volume load of 0,34 kg/(m 3 ×d) and the N-volume load of 0,16 kg/(m 3 ×d) are more or less at the upper limit of the conditions required for complete N-elimination. These ratios are also reflected in the process results ( ), especially resulting in frequently higher nitrate concentrations due to the limited carbon reserve. Table 4-14Properties of the treated effluent at the Plattling animal carcass disposal plant Table 4-14 Properties of the treated effluent at the Plattling animal carcass disposal plant Parameters Average Minimum - Maximum BSB5 homogenised mg/l 4,9 1 - 16 COD homogenised mg/l 52,5 34 - 75 NH4 -N mg/l 7,6 1 - 27 NO3 -N mg/l 39 1,2 - 99 NO2 -N mg/l 0,45 0,03 - 1,2 P total mg/l 11,9 0,9 - 28 GF 2 2 2 At the Brögbern animal flour factory, an anaerobic high performance system was com- missioned in 1989 with the aim of alleviating the pressure on the aerobic clarification plant. In the interim, the plant has been expanded further through a second, substantially larger reactor. Both are fixed bed circulation reactors in up-flow operation, filled with sin- tered glass Raschig rings (Siran ® high performance carrier material by the company Schott). This material is much more densely packed than the plastic material described and therefore allows higher COD volume loads (Table 4-15). The smaller reactor was ear- lier operated with a pre-acidification process and mainly served the purpose of anaerobic treatment of the blood process water. The entire effluent is now led through the two an- aerobic reactors, during which process nitrogen is initially eliminated from the dryer va- pours through ammonia conversion.
Teil 3 Seite 4-52 Table 4-15 Dimensional and performance data of the anaerobic reactors of the Brögbern animal carcass disposal plant Effective fixed bed volume 20 m 3 + 100 m 3 Specific surface area 30.000 m 2 / m 3 Dwell time 11 -15 h in the fixed bed reactor Internal cycle 3.000 - 4.000 % COD – inflow concentration 10.000 - 90.000 mg/l Ammonia - N inflow concentration 1.000 - 4.500 mg/l COD volume load approx. 14 kg/(m 3 ·d) COD decomposition performance 60 - 90% Reference literature 4.5.4 End of Pipe Technique 4.5.4.1 Agricultural reuse of organic liquids Definition Agricultural reuse is defined as spreading organic liquids (e.g. potato fruit juice, wheat starch process water) and biosolids (e.g. sewage sludge, composts) from food and drink processing plants on the soil making use of the agronomic value of these wastes for reuse as fully biodegradable fertilisers for crops and for the microbiological fauna of the soil without a negative influence to the environment (e.g. soils, groundwater). This agricultural reuse is also named as land spreading. Agricultural reuse is therefore different from land irrigation that is characterised by the spraying and discharging of waste water and water on the soil without control of environ- mental impacts. In this case, depending on the quality of the (waste) water, well water and soil can be contaminated. Objective The purpose of the agricultural reuse is to spread liquids and biosolids on agricultural fields, where the natural content of nutrients functions as fertilisers for crops and for mi- croorganisms where crops or soils have specific needs for nutrients. Indeed, organic liquids and biosolids from the food and drink industries are characterised by a high load of organic material. These liquids and biosolids contain not only carbon but also nitrogen and phosphorous bound to these organic matters as well as minerals. Pol- lutants are negligible.
- Seite 227 und 228: Liquid phase from the dewatering (y
- Seite 229 und 230: Teil 3 Seite 4-2 - Re- use of salt
- Seite 231 und 232: [to be completed] Main achieved env
- Seite 233 und 234: Teil 3 Seite 4-6 - Efficient use an
- Seite 235 und 236: Teil 3 Seite 4-8 heat exchangers, p
- Seite 237 und 238: Teil 3 Seite 4-10 The situation wit
- Seite 239 und 240: Teil 3 Seite 4-12 rect evaporation
- Seite 241 und 242: Teil 3 Seite 4-14 Additional heat e
- Seite 243 und 244: Weight loss after 24 hours Temperat
- Seite 245 und 246: 4.2.5 Evisceration Reference to act
- Seite 247 und 248: Achieved environmental benefits Cro
- Seite 249 und 250: 4.5.1 Mechanical treatment 4.5.1.1
- Seite 251 und 252: Teil 3 Seite 4-24 Both in terms of
- Seite 253 und 254: Teil 3 Seite 4-26 4.5.2.1 Ammoniaca
- Seite 255 und 256: Teil 3 Seite 4-28 Brögbern animal
- Seite 257 und 258: Teil 3 Seite 4-30 The decision depe
- Seite 259 und 260: Teil 3 Seite 4-32 closed area can b
- Seite 261 und 262: Teil 3 Seite 4-34 coincides with th
- Seite 263 und 264: Teil 3 Seite 4-36 At a slaughterhou
- Seite 265 und 266: Age of sludge (tTS) Is this of spec
- Seite 267 und 268: Example plants Teil 3 Seite 4-40 Co
- Seite 269 und 270: BSB5 - load Bd (BSB ) NH4 -N - load
- Seite 271 und 272: Fe Fl Fe Fl P D MB Teil 3 Seite 4-4
- Seite 273 und 274: Teil 3 Seite 4-46 Parameters Unit M
- Seite 275 und 276: Teil 3 Seite 4-48 To optimise the m
- Seite 277: Driving force for implementation Ex
- Seite 281 und 282: Teil 3 Seite 4-54 liquid fertiliser
- Seite 283 und 284: - No cross media effects Teil 3 Sei
- Seite 285 und 286: Teil 3 Seite 4-58 3. Filtermaterial
- Seite 287 und 288: Decomposition level Measure- Teil 3
- Seite 289 und 290: Teil 3 Seite 6-2 FAT/ HEAT TRANSFER
- Seite 291 und 292: Teil 3 Seite 6-4 Clarification plan
- Seite 293 und 294: Teil 3 Seite 6-6 ENERGY FAT/ HEAT C
- Seite 295 und 296: Teil 3 Seite 6-8 ENERGY/ STEAM INPU
- Seite 297 und 298: Teil 3 Seite 6-10 water if necessar
- Seite 299 und 300: Teil 3 Seite 6-12 - In- vessel comp
- Seite 301 und 302: Teil 3 Seite 6-14 For 1000 kg of de
- Seite 303 und 304: Teil 3 Seite 6-16 Liming is usually
- Seite 305 und 306: Teil 3 Seite 6-18 ceous earth filte
- Seite 307 und 308: See description under 1 Limed bone
- Seite 309 und 310: H Concentration See description und
- Seite 311 und 312: Teil 3 Seite 6-24 The excess acid i
- Seite 313 und 314: Teil 3 Seite 7-1 7 CURRENT CONSUMPT
- Seite 315 und 316: 7.1.1 Rendering 7.1.1.1 Water Teil
- Seite 317 und 318: Teil 3 Seite 7-5 - Cleaning wastewa
- Seite 319 und 320: Teil 3 Seite 7-7 Table 7-5 shows th
- Seite 321 und 322: 7.1.2 Fat melting 7.1.3 Fish meal a
- Seite 323 und 324: Teil 3 Seite 8-1 8 TECHNIQUES TO CO
- Seite 325 und 326: Reference literature Teil 3 Seite 8
- Seite 327 und 328: Teil 3 Seite 8-5 Corporate clarific
Teil 3 Seite 4-52<br />
Table 4-15 Dimensional and performance data of the anaerobic reactors of the Brögbern<br />
animal carcass disposal plant<br />
Effective fixed bed volume 20 m 3 + 100 m 3<br />
Specific surface area 30.000 m 2 / m 3<br />
Dwell time 11 -15 h in the fixed bed reactor<br />
Internal cycle 3.000 - 4.000 %<br />
COD – inflow concentration 10.000 - 90.000 mg/l<br />
Ammonia - N inflow concentration 1.000 - 4.500 mg/l<br />
COD volume load approx. 14 kg/(m 3 ·d)<br />
COD decomposition performance 60 - 90%<br />
Reference literature<br />
4.5.4 End of Pipe Technique<br />
4.5.4.1 Agricultural reuse of organic liquids<br />
Definition<br />
Agricultural reuse is defined as spreading organic liquids (e.g. potato fruit juice, wheat<br />
starch process water) and biosolids (e.g. sewage sludge, composts) from food and drink<br />
processing plants on the soil making use of the agronomic value of these wastes for reuse<br />
as fully biodegradable fertilisers for crops and for the microbiological fauna of the soil<br />
without a negative influence to the environment (e.g. soils, groundwater). This agricultural<br />
reuse is also named as land spreading.<br />
Agricultural reuse is therefore different from land irrigation that is characterised by the<br />
spraying and discharging of waste water and water on the soil without control of environ-<br />
mental impacts. In this case, depending on the quality of the (waste) water, well water and<br />
soil can be contaminated.<br />
Objective<br />
The purpose of the agricultural reuse is to spread liquids and biosolids on agricultural<br />
fields, where the natural content of nutrients functions as fertilisers for crops and for mi-<br />
croorganisms where crops or soils have specific needs for nutrients.<br />
Indeed, organic liquids and biosolids from the food and drink industries are characterised<br />
by a high load of organic material. These liquids and biosolids contain not only carbon but<br />
also nitrogen and phosphorous bound to these organic matters as well as minerals. Pol-<br />
lutants are negligible.